JPH0417278Y2 - - Google Patents
Info
- Publication number
- JPH0417278Y2 JPH0417278Y2 JP1987157725U JP15772587U JPH0417278Y2 JP H0417278 Y2 JPH0417278 Y2 JP H0417278Y2 JP 1987157725 U JP1987157725 U JP 1987157725U JP 15772587 U JP15772587 U JP 15772587U JP H0417278 Y2 JPH0417278 Y2 JP H0417278Y2
- Authority
- JP
- Japan
- Prior art keywords
- tank
- pressurized
- aeration tank
- pressurized aeration
- circulation pipe
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Activated Sludge Processes (AREA)
- Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
Description
【考案の詳細な説明】
(産業上の利用分野)
本考案は有機廃水の処理装置に係り、加圧曝気
槽内にエアを送り、該エアを微細気泡に変えて加
圧曝気槽内に拡散させ、生物酸化を進行させるよ
うにしたものである。[Detailed description of the invention] (Industrial application field) This invention relates to an organic wastewater treatment device, in which air is sent into a pressurized aeration tank, and the air is converted into fine bubbles and diffused into the pressurized aeration tank. It is designed to allow biological oxidation to proceed.
(従来例)
し尿や工場廃水のような有機廃水を加圧曝気槽
において曝気して生物酸化を進行させた後、浮上
分離槽において汚泥と清浄水を分離する廃水処理
装置の該加圧曝気槽として、ラインミキサを使用
するものが知られている(特公昭57−31959号公
報)。このラインミキサは、例えば特公昭36−
17790号公報に開示されているように、ポンプ作
用を兼ねた攪拌用羽根車と吐出ポンプ用羽根車と
を同一軸に嵌装した回転部と、循環流路を有する
攪拌室と吐出ポンプの渦室とを備え、かつ一方に
吸込口を他方に吐出口を備えた外筐との二部より
なる構造を有するものである。(Conventional Example) A pressurized aeration tank of a wastewater treatment device in which organic wastewater such as human waste or factory wastewater is aerated in a pressurized aeration tank to promote biological oxidation, and then sludge and clean water are separated in a flotation tank. There is a known method using a line mixer (Japanese Patent Publication No. 57-31959). This line mixer is, for example,
As disclosed in Publication No. 17790, there is a rotating part in which a stirring impeller that also serves as a pump and an impeller for a discharge pump are fitted on the same shaft, a stirring chamber having a circulation flow path, and a vortex of the discharge pump. It has a structure consisting of two parts: an outer casing with a suction port on one side and a discharge port on the other side.
(考案が解決しようとする問題点)
しかしながらかかるラインミキサは構造が複雑
であつて高価であり、かつ機械的にきわめて強力
な攪拌能力を必要とする等の問題点があつた。(Problems to be Solved by the Invention) However, such line mixers have problems such as being complicated in structure and expensive, and requiring extremely strong mechanical stirring ability.
(問題点を解決するための手段)
上記問題点を解決するために、本考案は有機廃
水を加圧曝気して生物酸化を行わせる加圧曝気槽
3と、該加圧曝気槽3から送り出された溶液を汚
泥と清浄水に分離する分離槽17とを有する有機
廃水の処理装置において、上記加圧曝気槽3の内
部に攪拌羽根4を配設するとともに、該加圧曝気
槽3内の溶液を循環させる循環ポンプP2と循環
パイプ5を設け、かつ該循環パイプ5の吸入部5
aを加圧曝気槽3の上部に接続するとともに、循
環パイプ5の吐出部5bを加圧曝気槽3の下部に
接続し、またこの吐出部5bを覆うようにデイフ
ユーザ8を配設するとともに、このデイフユーザ
8の近傍に超音波振動子7を配設し、且つ上記循
環パイプ5にエアを送るコンプレツサー10を接
続したものである。(Means for Solving the Problems) In order to solve the above problems, the present invention includes a pressurized aeration tank 3 in which organic wastewater is pressurized and aerated to perform biological oxidation, and a In an organic wastewater treatment apparatus having a separation tank 17 for separating a solution into sludge and clean water, a stirring blade 4 is disposed inside the pressurized aeration tank 3, and a stirring blade 4 is provided inside the pressurized aeration tank 3. A circulation pump P2 and a circulation pipe 5 for circulating the solution are provided, and a suction part 5 of the circulation pipe 5 is provided.
a to the upper part of the pressurized aeration tank 3, connect the discharge part 5b of the circulation pipe 5 to the lower part of the pressurized aeration tank 3, and arrange the diffuser 8 so as to cover the discharge part 5b, An ultrasonic vibrator 7 is disposed near the differential user 8, and a compressor 10 for sending air to the circulation pipe 5 is connected.
(作用)
上記構成において、加圧曝気槽3の内外には循
環ポンプP2の駆動により循環流が生じており、
コンプレツサー10から送出されたエアは循環パ
イプ5内においてこの循環流に混入され、加圧曝
気槽3の下部に流入する。循環パイプ5の吐出部
5bにおいて、エアは超音波振動子7の発する超
音波により微細気泡に変えられるとともに、デイ
フユーザ8により拡散される。したがつて槽3内
には微細気泡が多量にしかも均一に混入されるこ
ととなり、曝気効果は高められて生物酸化は著し
く進行し、BODは速かに除去される。特にこの
場合、超音波振動子7とデイフユーザ8は加圧曝
気槽3下部の吐出部5bの近傍に互いに近接して
設けられ、しかもデイフユーザ8は吐出部5bを
覆うように設けられているので、環環流が吐出部
5bから吐出される際に、超音波振動子7による
エアの粉砕とデイフユーザ8による拡散が同時に
且つ効率よく行われ、エアは瞬時に微細気泡とな
つて槽3内に拡散するので曝気効果はきわめて高
められ、迅速にBODを除去することができる。(Function) In the above configuration, a circulation flow is generated inside and outside the pressurized aeration tank 3 by driving the circulation pump P2,
The air sent out from the compressor 10 is mixed with this circulation flow in the circulation pipe 5 and flows into the lower part of the pressurized aeration tank 3. In the discharge section 5b of the circulation pipe 5, the air is converted into fine bubbles by the ultrasonic waves generated by the ultrasonic vibrator 7, and is diffused by the diffuser 8. Therefore, a large amount of fine bubbles are evenly mixed into the tank 3, the aeration effect is enhanced, biological oxidation progresses significantly, and BOD is rapidly removed. Particularly in this case, the ultrasonic vibrator 7 and the diffuser 8 are provided close to each other in the vicinity of the discharge part 5b at the bottom of the pressurized aeration tank 3, and the diffuser 8 is provided so as to cover the discharge part 5b. When the reflux is discharged from the discharge part 5b, the air is pulverized by the ultrasonic vibrator 7 and diffused by the diffuser 8 simultaneously and efficiently, and the air instantly becomes fine bubbles and diffuses into the tank 3. Therefore, the aeration effect is greatly enhanced and BOD can be quickly removed.
(実施例)
以下、図面を参照しながら本考案の実施例の説
明を行う。(Embodiments) Hereinafter, embodiments of the present invention will be described with reference to the drawings.
第1図は有機廃水の処理装置のフローチヤート
図であつて、1は除査し尿や工場廃水などの有機
廃水を貯えてモータM1により駆動される攪拌羽
根2により攪拌する攪拌槽である。3はポンプP
1により攪拌槽1から給送された廃水を加圧曝気
してBODを急速除去するための加圧曝気槽であ
り、該加圧曝気槽3は該ポンプP1とコンプレツ
サー10(後述)により2〜6気圧程度に加圧さ
れる。加圧曝気槽3を加圧するのは、空気をよく
溶け込ませて生物酸化を促進するためである。 FIG. 1 is a flowchart of an organic wastewater treatment apparatus, in which numeral 1 denotes a stirring tank in which organic wastewater such as excreta and industrial wastewater is stored and agitated by a stirring blade 2 driven by a motor M1. 3 is pump P
1 is a pressurized aeration tank for rapidly removing BOD by pressurizing and aerating the wastewater fed from the stirring tank 1, and the pressurizing aeration tank 3 is operated by the pump P1 and compressor 10 (described later). It is pressurized to about 6 atmospheres. The reason why the pressurized aeration tank 3 is pressurized is to dissolve air well and promote biological oxidation.
第2図に示すように、この加圧曝気槽3にはモ
ータM3により駆動される攪拌羽根4が配設され
ている。5は循環パイプ、P2は循環ポンプであ
つて、パイプ5の吸入部5aは槽3の上部に、ま
た吐出部5bは槽3の下部に接続されており、該
ポンプP2の駆動により槽3の内外に循環流を生
じ、吐出部5bから槽3に流入した溶液は槽3の
下部から上部へ上昇する。7,8は吐出部5bの
近傍に互いに近接して配設された超音波振動子と
デイフユーザである。このデイフユーザ8は、吐
出部5bを覆うように配設されている。10はコ
ンプレツサー、11は循環パイプ5の途中に設け
られたエジエクターであつて、コンプレツサー1
0により送出されたエアはエジエクター11によ
りパイプ5内を槽3へ向つて流れる循環流に混入
され、吐出部5bから槽3に流入するが、ここで
エアは超音波振動子7の発する超音波による粉砕
されて微細気泡に変えられるとともに、デイフユ
ーザ8により拡散され、槽3内に多量かつ均一に
溶け込んで曝気効果が上げられ、生物酸化は著し
く進行してBODは速かに除去される。特にこの
場合、超音波振動子7とデイフユーザ8は加圧曝
気槽3下部の吐出部5bの近傍に互いに近接して
設けられているので、超音波振動子7によるエア
の粉砕とデイフユーザ8による拡散は同時に行わ
れ、エアは瞬時に微細気泡となつて槽3内に拡散
するので曝気効果はきわめて高められ、迅速に
BODを除去することができる。しかも、デイフ
ユーザ8は吐出部5bを覆うように設けられてい
るので、吐出部5bから吐出されて微細気泡が混
合された循環流を、槽3内に効率よく拡散でき
る。12は槽3内の溶液の一部を攪拌槽1に戻す
ためのパイプである。なお第2図において、説明
上不要な配管は省略している。 As shown in FIG. 2, this pressurized aeration tank 3 is provided with stirring blades 4 driven by a motor M3. 5 is a circulation pipe, and P2 is a circulation pump. The suction part 5a of the pipe 5 is connected to the upper part of the tank 3, and the discharge part 5b is connected to the lower part of the tank 3. The pump P2 is driven to pump the tank 3. Circulating flow is generated inside and outside, and the solution flowing into the tank 3 from the discharge part 5b rises from the bottom to the top of the tank 3. Reference numerals 7 and 8 denote an ultrasonic transducer and a diffuser which are arranged close to each other in the vicinity of the discharge section 5b. This differential user 8 is arranged so as to cover the discharge section 5b. 10 is a compressor, 11 is an ejector provided in the middle of the circulation pipe 5, and the compressor 1
The air sent out by the ultrasonic transducer 7 is mixed into the circulating flow flowing through the pipe 5 toward the tank 3 by the ejector 11, and flows into the tank 3 from the discharge part 5b. The BOD is crushed into fine bubbles by the diffuser 8 and diffused by the diffuser 8, and is dissolved uniformly in a large amount in the tank 3, increasing the aeration effect, and the biological oxidation progresses significantly to rapidly remove BOD. Particularly in this case, the ultrasonic vibrator 7 and the diffuser 8 are provided close to each other in the vicinity of the discharge part 5b at the bottom of the pressurized aeration tank 3, so that the ultrasonic vibrator 7 crushes the air and the diffuser 8 diffuses the air. are carried out at the same time, and the air instantly becomes fine bubbles and diffuses into the tank 3, so the aeration effect is extremely enhanced and the air is quickly
BOD can be removed. Moreover, since the diffuser 8 is provided so as to cover the discharge part 5b, the circulating flow discharged from the discharge part 5b and mixed with fine bubbles can be efficiently diffused into the tank 3. 12 is a pipe for returning a part of the solution in the tank 3 to the stirring tank 1. In FIG. 2, unnecessary piping for explanation is omitted.
15は脱気槽であつて、モータM2により駆動
される攪拌羽根16が配設されており、加圧曝気
槽3から送られてきた溶液を攪拌してチツソガス
のような気泡を除去する。17は分離槽、18は
加圧水槽であり、ポンプP3により脱気槽15か
ら送られた溶液と加圧水槽18から送られた加圧
水は途中の合流部19で合流し、該分離槽17の
前部に流入する。分離槽17の内部には仕切壁2
0,21,22が配設さており、水は仕切壁2
0,21を越流し、また仕切壁22を潜流してほ
ぼ清浄化された水はパイプ23により一次処理水
として排出される。また浮上した汚泥は掻出装置
24により側方の汚泥槽25へ掻き出され、、パ
イプ26を通して活性汚泥として上記攪拌槽1へ
返送される。また清浄水の一部は、ポンプP4に
より加圧水槽18へ送られる。加圧水槽18には
上記コンプレツサー10からエアが送られてお
り、加圧水槽18内は気泡を多量に含んだ加圧水
が生成されるが、この加圧水は上述のように脱気
槽15から送られた溶液と混合されて分離槽17
へ入り、汚泥は気泡が付着して浮上し、上述のよ
うに掻上装置24に掻き出される。 Reference numeral 15 denotes a deaeration tank, which is provided with a stirring blade 16 driven by a motor M2, which stirs the solution sent from the pressurized aeration tank 3 to remove air bubbles such as titanium gas. 17 is a separation tank, 18 is a pressurized water tank, and the solution sent from the deaeration tank 15 by the pump P3 and the pressurized water sent from the pressurized water tank 18 are joined at a confluence part 19 in the middle, and the front part of the separation tank 17 is flows into. There is a partition wall 2 inside the separation tank 17.
0, 21, and 22 are installed, and the water is separated from the partition wall 2.
0, 21 and submerged through the partition wall 22, the almost purified water is discharged through a pipe 23 as primary treated water. Further, the floating sludge is scraped out by a scraping device 24 to a side sludge tank 25, and is returned to the stirring tank 1 as activated sludge through a pipe 26. A part of the clean water is also sent to the pressurized water tank 18 by the pump P4. Air is sent to the pressurized water tank 18 from the compressor 10, and pressurized water containing a large amount of air bubbles is generated in the pressurized water tank 18, but this pressurized water is mixed with the solution sent from the degassing tank 15 as described above. mixed with separation tank 17
The sludge enters the sludge, floats with air bubbles attached thereto, and is scraped out by the scraping device 24 as described above.
(考案の効果)
以上のように本考案によれば、コンプレツサー
10により循環流に混入されて吐出部5bから加
圧曝気槽3内に流入したエアは、超音波振動子7
の発する超音波により微細気泡に変えられるとと
もに、デイフユーザ8により拡散されて、槽3内
に多量にしかも均一に混入されることとなり、曝
気効果は高められて生物酸化は著しく進行し、
BODを速かに除去することができる。特にこの
場合、超音波振動子7とデイフユーザ8は加圧曝
気槽3下部の吐出部5bの近傍に互いに近接して
設けているので、超音波振動子7によるエアの粉
砕とデイフユーザ8による拡散は同時にしかも効
率よく行われ、エアは瞬時に微細気泡となつて槽
3内に拡散するので曝気効果はきわめて高められ
る。また循環流に混合された微細気泡は長く槽内
に滞溜するので、酸素利用効率は高くなり、かつ
コンプレツサー10からエア供給量が少くても十
分な曝気効果をあげることができ、更には酸素供
給速度も大きくなるため加圧曝気槽3内の活性汚
泥濃度も高く保つことができ、高濃度有機廃水の
処理も可能となる。(Effect of the invention) As described above, according to the invention, the air mixed into the circulation flow by the compressor 10 and flowing into the pressurized aeration tank 3 from the discharge part 5b is transferred to the ultrasonic vibrator 7.
They are converted into fine bubbles by the ultrasonic waves emitted by the diffuser 8, and are diffused by the diffuser 8 and mixed uniformly into the tank 3 in large quantities, increasing the aeration effect and significantly progressing biological oxidation.
BOD can be quickly removed. Particularly in this case, since the ultrasonic vibrator 7 and the diff user 8 are provided close to each other near the discharge part 5b at the bottom of the pressurized aeration tank 3, the pulverization of the air by the ultrasonic vibrator 7 and the diffusion by the diff user 8 are Simultaneously and efficiently, the air instantly becomes fine bubbles and diffuses into the tank 3, so the aeration effect is extremely enhanced. In addition, since the fine bubbles mixed with the circulating flow remain in the tank for a long time, the oxygen utilization efficiency is high, and even with a small amount of air supplied from the compressor 10, a sufficient aeration effect can be achieved. Since the supply rate is also increased, the activated sludge concentration in the pressurized aeration tank 3 can be kept high, and it is also possible to treat high-concentration organic wastewater.
図は本考案の実施例を示すものであつて、第1
図はフローチヤート図、第2図は加圧曝気槽の断
面図である。
3……加圧曝気槽、4……攪拌羽根、5……循
環パイプ、5a……吸入部、5b……吐出部、7
……超音波振動子、8……デイフユーザ、10…
…コンプレツサー、17……分離槽、P2……循
環ポンプ。
The figure shows an embodiment of the present invention.
The figure is a flowchart, and FIG. 2 is a sectional view of the pressurized aeration tank. 3... Pressurized aeration tank, 4... Stirring blade, 5... Circulation pipe, 5a... Suction part, 5b... Discharge part, 7
...Ultrasonic transducer, 8...Diff user, 10...
...Compressor, 17...Separation tank, P2...Circulation pump.
Claims (1)
圧曝気槽3と、該加圧曝気槽3から送り出された
溶液を汚泥と清浄水に分離する分離槽17とを有
する有機廃水の処理装置において、上記加圧曝気
槽3の内部に攪拌羽根4を配設するとともに、該
加圧曝気槽3内の溶液を循環させる循環ポンプP
2と循環パイプ5を設け、かつ該循環パイプ5の
吸入部5aを加圧曝気槽3の上部に接続するとと
もに、循環パイプ5の吐出部5bを加圧曝気水槽
3の下部に接続し、またこの吐出部5bを覆うよ
うにデイフユーザ8を配設するとともに、このデ
イフユーザ8の近傍に超音波振動子7を配設し、
且つ上記循環パイプ5にエアを送るコンプレツサ
ー10を接続したとを特徴とする有機廃水の処理
装置。 An organic wastewater treatment device having a pressurized aeration tank 3 in which organic wastewater is pressurized and aerated to perform biological oxidation, and a separation tank 17 in which a solution sent out from the pressurized aeration tank 3 is separated into sludge and clean water. In addition to disposing stirring blades 4 inside the pressurized aeration tank 3, a circulation pump P circulates the solution in the pressurized aeration tank 3.
2 and a circulation pipe 5 are provided, and the suction part 5a of the circulation pipe 5 is connected to the upper part of the pressurized aeration tank 3, and the discharge part 5b of the circulation pipe 5 is connected to the lower part of the pressurized aeration tank 3. A differential user 8 is disposed so as to cover the discharge portion 5b, and an ultrasonic vibrator 7 is disposed near the differential user 8,
An organic wastewater treatment apparatus characterized in that a compressor 10 for sending air is connected to the circulation pipe 5.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP1987157725U JPH0417278Y2 (en) | 1987-10-15 | 1987-10-15 |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP1987157725U JPH0417278Y2 (en) | 1987-10-15 | 1987-10-15 |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH0161998U JPH0161998U (en) | 1989-04-20 |
| JPH0417278Y2 true JPH0417278Y2 (en) | 1992-04-17 |
Family
ID=31437421
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP1987157725U Expired JPH0417278Y2 (en) | 1987-10-15 | 1987-10-15 |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0417278Y2 (en) |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6154288A (en) * | 1984-08-21 | 1986-03-18 | Nippon Kokan Kk <Nkk> | Closed water purification equipment |
| JPH067909B2 (en) * | 1985-03-30 | 1994-02-02 | 大阪瓦斯株式会社 | Gas absorption method |
-
1987
- 1987-10-15 JP JP1987157725U patent/JPH0417278Y2/ja not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPH0161998U (en) | 1989-04-20 |
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